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Title:
METHOD AND APPARATUS FOR ACHIEVING ENHANCED OXYGEN MASS TRANSFER IN SLURRY SYSTEMS
Document Type and Number:
WIPO Patent Application WO/2001/018263
Kind Code:
A1
Abstract:
A method of oxidising a slurry containing solid reactants which includes the step of supplying a feed gas containing in excess of 21 % oxygen by volume, to the slurry. Preferably the feed gas contains more than 85 % oxygen by volume. The method includes the step of maintaining the dissolve oxygen concentration in the slurry within a desired range. An oxidation plant therefor includes a reactor vessel, an oxygen source, a device for measuring the dissolved oxygen concentration in the slurry and a control mechanism for adjusting the supply of oxygen in response to the measured dissolved oxygen concentration.

Inventors:
BASSON PETRUS (ZA)
DEW DAVID WILLIAM (ZA)
Application Number:
PCT/ZA2000/000165
Publication Date:
March 15, 2001
Filing Date:
September 06, 2000
Export Citation:
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Assignee:
BILLITON INTELLECTUAL PTY (NL)
BASSON PETRUS (ZA)
DEW DAVID WILLIAM (ZA)
International Classes:
C22B3/02; C22B3/04; C22B3/18; C22B11/08; C22B15/00; (IPC1-7): C22B3/00; C22B3/18; C22B3/02; C22B3/04
Foreign References:
US4732608A1988-03-22
US5007620A1991-04-16
US5919674A1999-07-06
FR2640284A11990-06-15
EP0808910A21997-11-26
GB2225256A1990-05-30
US4816234A1989-03-28
Other References:
DATABASE WPI Section Ch Week 199504, Derwent World Patents Index; Class D15, AN 1995-023284, XP002156625
Attorney, Agent or Firm:
MCCALLUM RADEMEYER & FREIMOND (Montague Ampie, John, P.O. Box 1130, 7 Maclyn Hous, Bordeaux 2125 Randburg, ZA)
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Claims:
CLAIMS
1. A method of oxidising a slurry containing solid reactants which includes the step of supplying a feed gas containing in excess of 21% oxygen by volume, to the slurry.
2. A method according to claim 1 wherein the feed gas contains in excess of 85% oxygen by volume.
3. A method according to claim 1 or 2 which includes the step of maintaining the dissolved oxygen concentration in the slurry within a desired range.
4. A method according to claim 3 wherein the said dissolved oxygen concentration is maintained in the range of from 0.2 x 10'kg/m'to 10 x 103 kg/m3.
5. A method according to claim 3 or 4 wherein the dissolved oxygen concentration is maintained within a desired range by at least one of the following: controlling the oxygen content of the feed gas, controlling the supply of feed gas to the slurry, and controlling the rate of feed of slurry to a reactor.
6. A method according to claim 3,4 or 5 wherein the dissolved oxygen concentration in the slurry is determined by one or more of the following: by direct measurement of the dissolved oxygen concentration in the slurry, by measurement of the oxygen in a gas above the slurry, and indirectly, by measurement of the oxygen content in offgas from the slurry.
7. A method according to any one of claims 1 to 6 which includes the step of controlling the carbon content of the slurry.
8. A method according to claim 7 wherein the said carbon content is controlled by one or more of the following: the addition of carbon dioxide gas to the slurry, and the addition of other carbonaceous material to the slurry.
9. A method according to any one of claims 1 to 8 which includes the step of controlling the carbon dioxide content of the feed gas in the range of from 0.5% to 20% by volume.
10. A method according to any one of claims 1 to 9 which includes the step of oxidising the slurry at a temperature in excess of 40 °C.
11. A method according to claim 10 wherein the said temperature is in the range of from 40°C to 100°C.
12. A method according to claim 11 wherein the said temperature is in the range of from 60°C to 85°C.
13. A method according to any one of claims 1 to 12 wherein the slurry is oxidised in a vessel which is substantially closed.
14. A method of oxygenating a slurry containing process reactants which includes the steps of maintaining the slurry at a temperature in excess of 40°C and controlling the dissolved oxygen concentration in the slurry within a predetermined range.
15. A method according to claim 14 wherein the said dissolved oxygen concentration is controlled by controlling the supply of oxygen to the slurry.
16. A method according to claim 15 wherein the oxygen is supplied to the slurry in the form of oxygen enriched gas or substantially pure oxygen.
17. A method according to any one of claims 14 to 16 wherein the said temperature is in the range of from 60°C to 85°C.
18. A method of enhancing the oxygen mass transfer coefficient from a gas phase to a liquid phase in a slurry which includes the step of supplying a feed gas containing in excess of 21% oxygen by volume, to the slurry.
19. A method according to claim 18 wherein the feed gas contains in excess of 85% oxygen by volume.
20. A method according to claim 18 or 19 which includes the step of raising the temperature of the slurry.
21. A method of oxidising an aqueous slurry containing solid reactants which includes the steps of: (a) oxidising the slurry at a temperature above 40°C, and (b) maintaining the dissolved oxygen concentration in the slurry in the range of from 0.2 x 10' kg/m'to 10 x 10'kg/m'.
22. A method according to claim 21 wherein the temperature is In tne range of from 60°C to 85°C.
23. A method according to claim 21 or 22 wherein the dissolved oxygen concentration is maintained by supplying gas containing in excess of 21% oxygen by volume to the slurry.
24. An oxidation plant which includes a reactor vessel, a source which feeds a slurry to the vessel, an oxygen source, a device which measures the dissolved oxygen concentration in the slurry in the vessel, and a control mechanism whereby, in response to the said measured dissolved oxygen concentration, the supply of oxygen from the oxygen source to the slurry is controlled to achieve a dissolved oxygen concentration in the slurry within a predetermined range.
Description:
A METHOD OF ACHIEVING ENHANCED OXYGEN MASS TRANSFER IN SLURRY SYSTEMS BACKGROUND OF THE INVENTION This invention relates to the transfer of oxygen from a gas phase to a liquid phase in a solid/liquid or slurry system operating at low or atmospheric pressures.

Many processes such as fermentation, sulphide mineral leaching and bioleaching are dependent on the transfer of oxygen from a gas phase to the liquid phase of a slurry system. Often the processes rely on sparging air into the process reactors at elevated temperatures, e. g. from 30°C to 100°C, or higher.

The use of high temperatures between 50°C and 100°C greatly increases the rate of reaction in most processes, for example in mineral leaching and bioleaching.

The solubility of oxygen is however limited at high temperatures and the rate of reaction becomes limited. In the case of using air for the supply of oxygen, the effect of limited oxygen solubility is such that the rate of reaction becomes dependent on, and is limited by, the rate of oxygen transfer from the gas to the liquid phase. Specific examples of this are cited in the literature for bioleaching applications SUMMARY OF THE INVENTION According to one aspect of the invention there is provided a method of treating a slurry containing reactants to be oxidised which includes the step of supplying a feed gas containing in excess of 21% oxygen by volume, to the slurry.

The slurry may be an aqueous slurry containing significant quantities of solid reactants.

As used herein the expression"oxygen enriched gas"is intended to include a gas, eg. air. which contains in excess of 21% oxygen by volume.. This is an oxygen content greater than the oxygen content of air. The expression"pure oxygen"is intended to include a gas which contains in excess of 85% oxygen by volume.

"Reactant", as used herein, includes a substance or material which requires the presence of oxygen to undergo a chemical reaction.

Preferably the feed gas which is supplied to the slurry contains in excess of 85% oxygen by volume ie. is substantially pure oxygen.

The method may include the step of maintaining the dissolved oxygen concentration in the slurry within a desired range which may be determined by the operating conditions and the type of reactants in the slurry. In oxidation processes limited by oxygen mass transfer, the applicant has established that a lower limit for the dissolved oxygen concentration to sustain oxidation, is in the range of from 0.2 x 10"'kg/m"to 4.0 x 10-' kg/m3. On the other hand if the dissolved oxygen concentration is too high the oxygen utilisation efficiency is reduced and the rate of reaction may be inhibited. The upper threshold concentration also depends on the nature of the process and on the reactants, but typically is in the range of from 4 x 10-3 kg/m3 to 10 x 10-' kg/m3.

Thus, preferably, the dissolved oxygen concentration in the slurry is maintained in the range of from 0.2 x 10-' kg/m3 to 10 x 10-3 kg/m3.

The method may include the steps of determining the dissolved oxygen concentration in the slurry and, in response thereto, of controlling at least one of the following : the oxygen content of the feed gas, the rate of supply of the feed gas to the slurry, and the rate of feed of slurry to a reactor.

The dissolved oxygen concentration in the slurry may be determined in any appropriate way, e. g. by one or more of the following: by direct measurement of the dissolved oxygen concentration in the slurry, by measurement of the oxygen content in gas above the slurry, and indirectly by measurement of the oxygen

content in off-gas from the slurry, taking into account the rate of oxygen supply, whether in gas enriched or pure form, to the slurry, and other relevant factors.

In many processes requiring oxygen supply from a gas phase carbon dioxide must also be supplied as a source of carbon, examples being bioleaching and certain fermentation operations. Thus, the method may include the step of controlling the carbon content of the slurry. This may be achieved by one or more of the following: the addition of carbon dioxide gas to the slurry, and the addition of other carbonaceous material to the slurry.

The method may extend to the step of controlling the carbon dioxide content of the feed gas to the slurry in the range of from 0.5% to 20% by volume. A suitable figure for bioleaching is of the order of 1% to 1.5% by volume. In the example of bioleaching, the level of the carbon dioxide is chosen to maintain high rates of microorganism growth and sulphide mineral oxidation.

The process to which the invention is applied, is preferably carried out at an elevated temperature. As stated hereinbefore in general the rate of reaction increases with an increase in operating temperature. As the addition of oxygen enriched gas or substantially pure oxygen to the slurry has a cost factor it is desirable to operate at a temperature which increases the reaction rate by an amount which more than compensates for the increase in operating cost. Thus, preferably, the process is carried out at a temperature in excess of 40°C.

The process may be carried out at a temperature of up to 100°C or more and preferably is carried out at a temperature which lies in a range of from 60°C to 85°C.

The slurry may be in a reactor tank or vessel which is open to atmosphere or substantially closed. In the latter case vents for off-gas may be provided from the reactor.

According to a different aspect of the invention there is provided a method of oxygenating a slurry containing process reactants which includes the steps of maintaining the slurry at a temperature in excess of 40°C and controlling the dissolved oxygen concentration in the slurry within a predetermined range.

The said dissolved oxygen concentration may be controlled by controlling the supply of oxygen to the slurry.

The oxygen may be supplied to the slurry in the form of oxygen enriched gas or substantially pure oxygen.

The said temperature is preferably in the range of 60°C to 85°C.

The invention specifically extends to a method of enhancing the oxygen mass transfer coefficient from a gas phase to a liquid phase of a solid/liquid slurry which includes the step of supplying a feed gas containing in excess of 21% oxygen by volume to the slurry.

The feed gas preferably contains in excess of 85% oxygen by volume.

The invention further extends to a method of oxygenating an aqueous slurry containing solid reactants which includes the steps of oxygenating the slurry at a temperature above 40°C and maintaining the dissolved oxygen concentration in the slurry in the range of from 0.2 x 10-'kg/m'to 10 x 10-3 kg/m'.

The dissolved oxygen concentration may be maintained by supplying gas containing in excess of 21% oxygen by volume to the slurry.

The invention is also intended to cover a process plant which includes a reactor vessel, a source which feeds a solid/liquid slurry to the vessel, an oxygen source, a device which measures the dissolved oxygen concentration in the slurry in the vessel, and a control mechanism whereby, in response to the said measure of dissolved oxygen concentration, the supply of oxygen from the oxygen source to the slurry is controlled to achieve a dissolved oxygen concentration in the slurry within a predetermined range.

Various techniques may be used for controlling the supply of oxygen to the slurry and hence for controlling the dissolved oxygen content or concentration in the slurry at a desired value. Use may for example be made of valves which are operated manually. For more accurate control use may be made of an automatic control system. These techniques are known in the art and are not further described herein.

For example use may be made of a dissolved oxygen probe to measure the dissolved oxygen concentration in the slurry directly. To achieve this the probe is immersed in the slurry. The dissolved oxygen concentration may be measured indirectly by using a probe in the reactor off-gas or by transmitting a sample of the off-gas, at regular intervals, to an oxygen gas analyser. Again it is pointed out that measuring techniques of this type are known in the art and accordingly any appropriate technique can be used.

A preferred approach to the control aspect is to utilise one or more probes to measure the dissolved oxygen concentration in the slurry, whether directly or indirectly. The probes produce one or more control signals which are used to control the operation of a suitable valve or valves, eg. solenoid valves, automatically so that the supply of oxygen to an air stream which is being fed to the slurry is varied automatically in accordance with real time measurements of the dissolved oxygen concentration in the slurry. A similar approach may be used to control the carbon dioxide content in the slurry.

Although it is preferred to control the addition of oxygen to a gas stream which is fed to the slurry a reverse approach may be adopted in that the oxygen supply rate to the reactor vessel may be maintained substantially constant and the rate of supply of the solid reactants in the slurry to the reactor vessel may be varied to achieve a desired dissolved oxygen concentration.

The invention is not limited to the actual control technique employed and is intended to extend to variations of the aforegoing approaches and to any equivalent process.

BRIEF DESCRIPTION OF THE DRAWINGS The invention is further described by way of example with reference to the accompanying drawings in which:

Figure 1 is a schematic representation of a portion of a plant in which the invention is carried out, and Figures 2,3 and 4 reflect various results and parameters obtained from operating a reactor using the principles of the invention.

DESCRIPTION OF PREFERRED EMBODIMENT General Principales The limitation of low oxygen solubility during a process involving oxidation in a slurry, using air, at high temperatures, which in turn limits the rate of reaction, requires enrichment of the air with oxygen ie. air with an oxygen content greater than 21% by volume, or the use of pure oxygen (defined as being greater than 85% oxygen by volume). The use of oxygen enriched air or pure oxygen overcomes the limited rate of reaction due to oxygen supply constraints, but has two major disadvantages: a) the provision of oxygen enriched air or pure oxygen is expensive and requires a high utilisation (>60%) of the oxygen to warrant the additional expense (3); and b) if the oxygen level in solution becomes too high the reaction rate may be reduced and oxygen utilisation decreases.

Therefore, in order to realise the benefits of high rates of reaction at high temperatures in commercial plants, the drawbacks of requiring expensive oxygen and the risk of failure if the dissolved oxygen levels become too high must be overcome.

The oxidation of solid reactants at an elevated temperature results in high rates of reaction, but is dependent on the supply of oxygen and possibly carbon dioxide in certain applications, to maintain high rates of reaction.

The absorption of oxygen and carbon dioxide in the bioleaching reactor is limited, in each case, by the rate of mass transfer from the gas phase into the solution phase. For oxygen the rate of oxygen absorption is defined by equation (1) as follows: R = M. (C*-CL) (1) where: R = Oxygen demand as mass (kg) per unit volume (m3) per unit time (s) (kg/m/s),

M = Oxygen mass transfer coefficient in reciprocal seconds (s'), C* = Saturated dissolved oxygen concentration as mass (kg) per unit volume (m') (kg/m'), and CL = Dissolved oxygen concentration in solution as mass (kg) per unit volume (m') (kg/m').

The factor (C*-CL) is referred to as the oxygen driving force. A similar equation may be used to describe the rate of carbon dioxide supply to the solution. If the sulphide mineral oxidation rate is increased the oxygen demand increases proportionately. To meet a higher oxygen demand either the oxygen mass transfer coefficient (M) or the oxygen driving force (C*-CL) must be increased.

An increase in the oxygen mass transfer coefficient may be achieved by increasing the power input to a mixer in the reactor. This improves gas dispersion in the sulphide mineral slurry. With this approach, however, an increase in the oxygen mass transfer coefficient of, for example, 40% requires an increase in the power input to the mixer by a factor of as much as 200%, with a commensurate increase in operating costs.

The oxygen driving force may be increased by increasing the saturated dissolved oxygen concentration C* and reducing the dissolved oxygen content or concentration C,.

The applicant has established that a lower limit for the dissolved oxygen concentration to sustain most oxidation reactions is in the range of from 0.2 x 10-'kg/m3 to 4.0 x 10-3 kg/m3. Thus, in order to provide an adequate, or optimum, supply of oxygen, the dissolved oxygen concentration in the sulphide mineral slurry must be monitored and, where appropriate, the addition of oxygen to the sulphide mineral slurry must be controlled in order to maintain the minimum dissolved oxygen concentration in solution at a value of from 0.2 x 10-3 kg/m3 to 4.0 x 10'3 kg/m'.

On the other hand the dissolved oxygen concentration must not exceed an upper threshold value at which the reaction rate is adversely affecte. It is pointed out that the upper threshold concentration depends on

the nature of the process and the reactants. A typical upper threshold value is in the range of from 4 x 10'" kg/m3 to 10 x 10~3 kg/m3, as for example in the application of bioleaching (4).

As has been previously indicated the rate of reaction which can be achieved when operating at a relatively low temperature of the order of from 40°C to 55°C, is limited. In order to increase the rate of oxidation it is desirable in many instances to make use temperatures in excess of 60°C. The optimum operating temperature is dependent on the nature of the process.

The applicant has established that the operation of the process, using a gas enriched with oxygen, or pure oxygen, as the oxidant, at elevated temperatures of from 40°C to 85C: increases the specific oxidation duty of the reactor considerably; results in an unexpected and significantly enhanced oxygen mass transfer rate ; increases the oxygen utilisation, providing that the dissolved oxygen concentration is controlled above the point where oxidation is prevented and below the point at which oxidation is inhibited; and the overall power required for oxidation is significantly reduced.

The controlled addition of oxygen enriched air or pure oxygen directly into the bioreactor improves the oxygen utilisation efficiency. In one example for bioleaching of mineral sulphides, the oxygen utilisation for a conventional commercial bioleach plant (at least 100m'in volume) operating at from 40°C to 45°C with air may be expected to achieve a maximum oxygen utilisation factor of from 40% to 50%. Consequently only 40% to 50% of the total mass of oxygen supplied to the bioleach plant is used to oxidise the sulphide minerals. With the method of the invention the oxygen utilisation is significantly higher, of the order of from 60% to 95%. The higher oxygen utilisation is achieved by controlled oxygen addition and results from the enhanced oxygen mass transfer rate and by operating at low dissolved oxygen concentrations in the solution phase.

It will be appreciated that although high oxygen demand in process reactors has come about primarily by the use of higher temperatures, rapid oxidation rates at temperatures below 60°C, will have similarly high oxygen

demands. The method of the invention is therefore not restricted to suit high temperature processes only, i. e. at temperatures above 60°C, but also low temperature processes from 30°C to 60°C.

Another advantage of using air enriched with oxygen or pure oxygen is that the evaporation losses are reduced, because there is less inert gas removing water vapour from the top of the reactor. This is particularly important in areas where water is scarce or expensive.

In carrying out the method of the invention the temperature of the slurry in the reactor may be controlled in any suitable way known in the art. In one example the reactor is insulated and heating takes place by means of energy which is released by the oxidation process. The temperature of the slurry is regulated using any suitabte cooling system, for example an internal cooling system.

In the specific application for bioleaching, Table 1 shows typical data for specific sulphide oxidation duty and oxygen utilisation, when bioleaching with air at 40°C to 45°C, in two commercial bioreactors, Plant A and Plant B respectively, (greater than 100m'in volume).

Table 1 Commercial Bioreactor Performance Results Description Units Plant A Plant 6 Reactortemperature °C 42 40 Reactor operating volume m 471 896 Oxygen37.943.6% Typical dissolved oxygen concentration mg/l 2.5 2. 7 Oxygen mass transfer coefficient s-1 0.047 0. 031 Specific oxygen demand kg/m Iday 21. 6 Si4.8 Specific sulphide oxidation duty kgfm »/day 8. 9 5.7 Specific power consumption per kgsulphide kWh/kgS'1. 71. 8 oxidised

At low temperatures (40°C-50°C), with air as the inlet gas, which applies to the results for the commercial reactors, Plant A and Plant B, presented in Table 1, the oxygen utilisations achieved are expected and the oxygen mass transfer coefficients (M) correspond to the applicant's design value. The applicant has determined that if the method of the invention were to be applied to Plant A, the plant performance would be significantly increased, as indicated by the results presented in Table 2.

Table 2 Predicted Improvement In Commercial Bioreactor Performance Units Plant A-typical Plant A-using the oftheoperationmethod invention °CReactortemperature 42 77 Microbial type strain-Acidithiobacillus Sulfolobus Inlet gas oxygen content % by volume 20.9 90.0 Oxygen utilisation % 37. 9 93.0 Typical dissolved oxygen concentration mg/I 2. 5 2.5 Specific oxygen demandkg/m/day21. 659. 5 Specific sulphide oxidation duty kg/m/ay 24.5 Specific power consumption per kg kWh/kgS'-1. 7 1. 2 sulphide oxidised The results clearly show the benefit of the invention in achieving higher rates of reaction by the combination of high temperature, adding oxygen enriched gas and by controlling the dissolved oxygen concentration above a predetermined low level (e. g. 0.2 x 10'"kg/m"to 4.0 x 10'"kg/m"). The specific oxidation duty of the reactor is increased by almost threefold. Clearly the upper dissolved oxygen concentration shouid not be increased above a value at which the reaction rate is reduced or at which oxygen utilisation is lowered.

Even though additional capital for the production of oxygen is required, the savings in reactor and other costs at least offset this additional expense. Additionally, in the case of bioleaching, the specific power consumption per kg sulphide oxidised is decreased by approximately one-third. In a plant oxidising 300 tonnes of sulphide per day, the power saving, assuming a power cost of US$0.05 per kWh, would amount to US$2.8 million per annum. The high oxygen utilisation and increased specific oxidation capacity of the

reactor represent in combination a considerable improvement over conventional low pressure oxidation reactors operating at lower temperatures, with oxygen supplied by air.

Particuiar Example Figure 1 of the accompanying drawings illustrates a non-limiting example of the invention and shows a plant 10 in which oxidation is carried out, in accordance with the principles of the invention.

The plant 10 includes a reactor 12 with an agitator or mixer 14 which is driven by means of a motor and gearbox assembly 16.

In use a tank or vessel 18 of the reactor contains a feed slurry 20. An impeller 22 of the agitator is immersed in the slurry and is used for mixing the slurry in a manner which is known in the art.

A probe 24 is immersed in the slurry and is used for measuring the dissolved oxygen concentration in the slurry. A second probe 26, inside the tank 18 above the surface level 28 of the slurry, is used for measuring the carbon dioxide content in the gas 30 above the slurry 20.

An oxygen source 32, a carbon dioxide source 34 and an air source 36 are connected through respective control valves 38,40 and 42 to a sparging system 44, positioned in a lower zone inside the tank 18, immersed in the slurry 20.

The probe 24 is used to monitor the dissolved oxygen concentration in the slurry 20 and provides a control signal to a control device 46. The control device controls the operation of the oxygen supply valve 38 in a manner which is known in the art but in accordance with the principles which are described herein in order to maintain a desired dissolved oxygen concentration in the slurry 20.

The probe 26 measures the carbon dioxide content in the gas above the slurry 20. The probe 26 provides a control signal to a control device 48. which, in turn, controls the operation of the valve 40 in order to control the addition of carbon dioxide from the source 34 to a gas stream flowing to the sparger 44.

The air flow rate from the source 36 to the sparger 44 is controlled by means of the valve 42. Normally the valve is set to provide a more or less constant flow of air from the source 36 to the sparger and the additions of oxygen and carbon dioxide to the air stream are controlled by the valves 38 and 40 respectively. Although this is a preferred approach to adjusting the oxygen and carbon dioxide contents in the air flow to the sparger other techniques can be adopted. For example it is possible, although with a lower degree of preference, to adjust the air stream flow rate and to mix the adjustable air stream with a steady supply of oxygen and a variable supply of carbon dioxide, or vice versa. Another possibility is to have two separate air stream flows to which are added oxygen and carbon dioxide respectively. Irrespective of the technique which is adopted the objective remains the same, namely to control the additions of oxygen and carbon dioxide to the slurry 20.

Slurry 50 is fed from a slurry feed source 52 through a control valve 54 and through an inlet pipe 56 into the interior of the tank 18. The slurry feed rate may be maintained substantially constant, by appropriate adjustment of the valve 54, to ensure that slurry is supplied to the tank 18 at a rate which sustains an optimum leaching rate. The supplies of air, oxygen and carbon dioxide are then regulated, taking into account the substantially constant slurry feed rate, to achieve a desired dissolved oxygen concentration in the slurry 20 in the tank, and a desired carbon dioxide content in the gas 30 above the slurry. Although this is a preferred approach it is apparent that the slurry feed rate could be adjusted, in response to a signal from the probe 24, to achieve a desired dissolved oxygen concentration in the slurry. In other words the rate of oxygen addition to the slurry may be kept substantially constant and the slurry feed rate may be varied according to requirement.

Another variation which can be adopted is to move the probe 24 from a position at which it is immersed in the slurry to a position designated 24A at which it is located in the gas 30 above the level 28. The probe then measures the oxygen contained in the gas above the slurry ie. the bioreactor off-gas. The oxygen content in

the off-gas can also be used as a measure to control the dissolved oxygen concentration in the slurry, taking any other relevant factors into account.

Conversely it may be possible to move the carbon dioxide probe 26 (provided it is capable of measuring the dissolved carbon dioxide content) from a position at which it is directly exposed to the gas 30 to a position designated 26A at which it is immersed in the slurry in the tank. The signal produced by the probe at the position 26A is then used, via the control device 48, to control the addition of carbon dioxide from the source 34 to the air stream from the source 36.

Although the carbon dioxide source 34, which provides carbon dioxide sn gas form, is readily controllable and represents a preferred way of introducing carbon into the slurry 20, it is possible to add suitable carbonate materials to the slurry 50 before feeding the slurry to the reactor. Carbonate material may also be added directly to the slurry 20 in the reactor. In other cases though there may be sufficient carbonate in the feed slurry so that it is not necessary to add carbon, in whatever form, to the slurry nor to control the carbon content in the slurry.

It is apparent from the aforegoing description which relates to the general principles of the invention that the supply of oxygen to the slurry is monitored and controlled to provide a desired dissolved oxygen concentration level in the slurry 20. This can be done in a variety of ways eg. by controlling one or more of the following in an appropriate manner namely: the slurry feed rate, the air flow rate from the source 36, the oxygen flow rate from the source 32, and any variation of the aforegoing.

The carbon dioxide flow rate is changed in accordance with the total gas flow rate to the sparger 44 in order to maintain a concentration in the gas phase, i. e. in the gas stream to the reactor, of from 0.5% to 5% carbon dioxide by volume. This carbon dioxide range has been found to maintain an adequate dissolved carbon dioxide concentration in the slurry, a factor which is important in achieving effective leaching.

The addition of oxygen to the slurry 20 is controlled in order to maintain the minimum dissolved oxygen concentration in solution at a value of from 0.2 x10'kg/mto4.0 x 10~3 kg/m3. The upper threshold value

depends on the nature of the process and of the reactants and typically is in the range of from 4 x 10"kg/m' to 10 x 10-3 kg/m3.

Figure 1 illustrates the addition of oxygen from a source 32 of pure oxygen. The pure oxygen can be mixed with air from the source 36. Any other suitable gas can be used in place of the air. The addition of oxygen to air results to what is referred to in this specification as oxygen enriched gas ie. a gas with an oxygen content in excess of 21% by volume. It is possible though to add oxygen substantially in pure form directly to the slurry. As used herein pure oxygen is intended to mean a gas stream which contains more than 85% oxygen by volume.

The temperature in the reactor or vessel may be controlled in any appropriate way using techniques which are known in the art. In one example the tank 18 is insulated and heating takes place by means of energy which is released by the oxidation reaction. The temperature of the slurry 20 is regulated using an internal cooling system 70 which includes a plurality of heat exchanger cooling coils 72 connected to an external heat exchanger 74.

The vessel 18 may be substantially sealed by means of a lid 80. Small vents 82 are provided to allow for the escape of off-gas. The off-gas may. if required, be captured or treated in any appropriate way before being released to atmoshpere. Alternatively, according to requirement, the tank 18 may be open to atmoshpere.

The rate of reaction will be increased at high temperature but the optimum operating temperature will be determined by the process. The applicant has found that in many cases a preferred operating temperature is above 60°C, for example in the range of 60°C to 85°C.

Although the benefit of adding oxygen to the slurry which is to be oxidised, by making use of oxygen enriched air or, more preferably, by making use of substantially pure oxygen ie. with an oxygen content in excess of 85%, is most pronounced at high temperatures at which greater oxidation rates are possible, a benefit is nonetheless to be seen when oxygen enriched air or substantially pure oxygen is added to the slurry at lower temperatures, of the order of 40°C or even lower. At these temperatures the reaction rates are lower than at

elevated temperatures and although an improvement results from using oxygen enriched air the cost thereof is generally not warranted by the relatively small increase in reaction rate.

Test Resuits The method of the invention has been demonstrated in a bioleaching application.

The importance of maintaining an adequate supply of oxygen and hence a sufficiently high dissolved oxygen concentration to sustain microorganism growth and mineral oxidation is shown in the results presented in Figure 2. If the dissolved oxygen concentration is allowed to d''op beicw 1.5 ppm, and particularly below 1.0 ppm, biooxidation becomes unstable, which is indicated by higher iron (II) concentrations in solution, of greater than 2 g/l. At consistent levels of biooxidation, achieved by maintaining a dissolved oxygen concentration above 1.5 ppm, in this experiment, iron (II) is rapidly oxidised to iron (III), and iron (II) concentrations remain generally below 1.0 g/l.

The results presented in Figure 2 were obtained from operation of a first or primary reactor of a continuous pilot plant treating a chalcopyrite concentrate at a feed solids concentration of 10% by mass and a temperature of 77°C, with Sulfolobus-like archaea.

The effect of increasing the oxygen content of the feed gas to a bioreactor and controlling the dissolved oxygen concentration, in accordance with the principles of the invention, was tested in an experiment using a 5M3 bioreactor which was operated with a continuous pyrite or blended pyrrhotite and pyrite flotation concentrate feed, at a temperature of about 77°C, using a mixed culture of Sulfolobus-like archaea and a solids density of 10% by mass. The carbon dioxide content in the bioleach inlet gas was controlled at a level of between 1 and 1.5 % by volume. The dissolved oxygen concentration was generally within the range 0.4 x 10~3 kg/m3 to 3.0 x 10-3 kg/m3. The results of the experiment are presented in Figure 3.

From the graphs presented in Figure 3 it is clear that, when sparging with air (enriched with carbon dioxide: 20.7% oxygen and 1.0% carbon dioxide), the maximum oxygen demand (directly proportional to the sulphide

oxidation duty) was limited to 11.3 kg/m3/day, since the dissolved oxygen concentration which was achievable using air only (i. e. not enriched with oxygen) was just sufficient to maintain micrccrganism growth.

By controlling the oxygen content of the inlet gas, the oxygen addition rate, and the cissolved oxygen concentration in the slurry in the range of 0.4 x 10'3 kg/m3 to 3.0 x 10-3 kg/m', the oxygen demand, i. e. the sulphide mineral oxidation rate, was increased dramatically. The dissolved oxygen concentration was controlled to a low value, but above the minimum limit for successful microorganism growth, so that the utilisation of oxygen was maximised. The results show the oxygen demand, or sulphide oxidation duty, was increased by over threefold. Thus by increasing the oxygen content in the inlet gas from 20.7% to a maximum of 90.8% the specific oxygen demand was increased from 11.3 kg/m3/day to 33.7 kg/m3/day In addition, by controlling the dissolved oxygen concentration to a low value, but above the minimum value for sustained microorganism growth, the oxygen utilisation was maximised. The oxygen utilisation showed a general increase with an increase in the oxygen content of the inlet gas from 29% (for an inlet gas oxygen content of 20.7%) to 91% (for inlet gas containing 85.5% oxygen).

The high oxygen utilisations achieved of well over 60% are much better than expected. Analysis of the results indicates that the oxygen mass transfer coefficient (M), as defined by equation (1), is significantly and unexpectedly enhanced for operation of the bioreactor at a high temperature (77°C) and with a high oxygen content in the inlet gas (from 29% to 91% in the experiment). In fact, the oxygen mass transfer coefficient (M) is increased by a factor of 2.69, on average, compared to the applicant's design value. This enhancement is after considering the improvement in the mass transfer coefficient due to temperature, which would be expected to increase the value of M by a factor of 1.59 for a temperature increase from 42°C to 77°C, according to the temperature correction factor proposed by Smith et al (5). This correction factor has been demonstrated experimentally to be valid for a temperature in the range of from 15°C to 70°C (6) The determination of the enhanced oxygen mass transfer coefficient is shown from the results presented in Figure 4, where the oxygen demand divided by the design oxygen mass transfer coefficient (Maesqn) is plotted against the oxygen driving force, as defined in equation (1). The slope of the regression line plotted through the data indicates the enhancement in the oxygen mass transfer coefficient by a factor of 2.69.

Example 1 A reactive sulphide mineral such as cobalt sutphide, when leached under atmospheric conditions at a temperature of about 80°C, has a high oxygen demand in excess of 30kg/m3 per day. The method of the invention is expected to improve the oxygen utilisation efficiency, and significantly reduce the energy requirement for oxygen supply of this process, as indicated by the predicted results presented in Table 3.

Table 3 Example of Method of Invention Applied to Chemical Leaching of Cobalt Sulphide Description Units Standard Enhanced OperationOperation* Specific Oxygen Demand kg/m'/aay 60. 5 60.5 Reactor8080°C Reactor2020m3 Oxygen content feed gas % 20. 9 90 OxygenUtilisation % 21. 4 55 Typical dissolved oxygen concentrationppm1. 37.6 Specific power duty (kWh per kg oxygen) kWh/kgO2 1. 6 0.

^ according to the method of the invention.

The results show that by applying the method of the invention the oxygen utilisation has been more than doubled from 21% to 55 %. The specific power consumption for oxygen transfer has been decreased by a factor of 10 i. e. from 1.6 kWh/kgO2 to 0.14 kWh/kgO2. In terms of known methods for oxygen supply and control where no enhancement of the oxygen mass transfer coefficient is achieved the expected power consumption, using the method of the invention, would be less than one third of what otherwise would be the case.

The method of the invention is also useful in aerobic processes other than bioleaching applications such as fermentation processes and the production of Serine Alkaline Protease by Bacillus Licheniformis 'at iow

temperatures (35°C to 40°C). In this process it has been shown (7) that the rate of reac: : on may become limited by the oxygen mass transfer rate. Therefore the use of the method of the invention... nich gives rise to a significant improvement in the oxygen mass transfer rate, may be expected to improve substantially the production rate of Serine Alkaline Protease using the aforementioned process (7).

Another example known in the fermentation industry, where oxygen supply and control are critical, is the production of Pichia pastoris.

In all cases of fermentation which require oxygen supply the use of the method of the invention whereby the oxygen mass transfer coefficient is increased by a factor of up to 3 (as may be expected from the bioleaching example referred to earlier herein) reduced capital and operating costs will be achieved as a consequence thereof.

REFERENCES 1. Bailey, A. D., and Hansford, G. S., (1996), Oxygen mass transfer limitation cf ba cr bio-oxidation at high solids concentration. Minerals Eng., 7 (23), pp293-303.

2. Myerson, A. S., (1981), Oxygen mass transfer requirements during the growth of Thiobacillus ferrooxidans on iron pyrite, Biotechnol, Bioeng., Vol 23, pp1413.

3 Peter Greenhalgh. and lan Ritchie, (1999); Advancing Reactor Design For The Gold Bioleach Process ; Minproc Ltd, Biomine 99,23-25 Aug 1999, Perth Australia, pp52-60.

4. Brock Biology of Microogranisms, Eight Edition, 1997., Madigan M. T., Martinko J. M., Parker J., Prentia Hall International, Inc., London.

5. J. M. Smith, K van't Riet and J. C. Middleton, (1997), Scale-Up of Agitated Gas-Liquid Reactors for Mass Transfer, in Proceedings of the 2nd European Conference on Mixing, Cambridge, England, 30 March-1 April 1997, pp. F4-51-F4-66.

6. Boogerd, F. C., Bos, P., Kuenen, J. G., Heijnen, J. J. & Van der Lans, R. G. J.

M, Oxygen and Carbon Dioxide Mass Transfer and the Aerobic, Autotrophic Cultivation of Moderate and Extreme Thermophiles A Case Study Related to the Microbial Desulfurization of Coal, Biotech.

Bioeng., 35,1990, p. 1111-1119.

7. Pinar Calih, Guzide Calih, Tuncer H Ozdamar, Oxygen-transfer Strategy and its Regulation Effects in Serine Alkaline Protease Production by Bacillus Licheniformis, Biotechnology and Bioengineering, Vol. 69, No. 3, Aug. 5,2000, pp. 301-311.